Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Amphibia Anura Hylidae

Scientific Name: Osteopilus septentrionalis
Species Authority: (Duméril & Bibron, 1841)
Common Name(s):
English Cuban Treefrog, Giant Tree-frog
Hyla dominicensis subspecies insulsa Mittleman, 1950
Hyla dominicensis subspecies septentrionalis Mertens, 1938
Hyla insulsa (Cope, 1863)
Hyla microterodisca Werner, 1921
Hyla schebestana Werner, 1917
Hyla septentrionalis Duméril & Bibron, 1841
Trachycephalus insulsus Cope, 1863
Trachycephalus marmoratus Duméril & Bibron, 1841
Trachycephalus septentrionalis (Duméril and Bibron, 1841)
Trachycephalus wrightii Cope, 1863
Taxonomic Source(s): Frost, D.R. 2013. Amphibian Species of the World: an Online Reference. Version 5.6 (9 January 2013). Electronic Database. American Museum of Natural History, New York, USA. Available at:

Assessment Information [top]

Red List Category & Criteria: Least Concern ver 3.1
Year Published: 2010
Date Assessed: 2008-11-13
Assessor(s): Blair Hedges, Luis Díaz, Beatrice Ibéné, Rafael Joglar, Robert Powell, Federico Bolaños, Gerardo Chaves
Reviewer(s): Global Amphibian Assessment Coordinating Team (Simon Stuart, Janice Chanson, Neil Cox and Bruce Young)
Listed as Least Concern in view of its wide distribution, tolerance of a broad range of habitats, presumed large population, and because it is unlikely to be declining to qualify for listing in a more threatened category.
Previously published Red List assessments:
2008 Least Concern (LC)
2004 Least Concern (LC)

Geographic Range [top]

Range Description: This species occurs on Cuba, the Isla de Juventud (Cuba), Archipelago de los Canarreos (Cuba), the Archipelago de Sabana-Camaguey (Cuba), Cayos de San Felipe (Cuba), the Cayman Islands, and the following places in the Bahamas: Little and Great Bahamas Banks, Long Island, Cat Island, Conception Island, Rum Cay, San Salvador, Crooked-Acklands Bank, and Great Inagua Island. It is introduced on Puerto Rico, the US Virgin Islands (St. Croix, St John, St Thomas), Tortola, Virgin Gorda, Beef Island and Peter Island (British Virgin Islands), the Turks and Caicos Islands, the Florida Keys and mainland Florida (USA), Hawaii (USA), Anguilla, St Martin (France portion, not yet in Netherlands portion), St Barthelemy, Bonaire, and Limon, Costa Rica (Gerardo Chaves pers. comm.). It occurs from sea level up to 1,110m asl.
Countries occurrence:
Bahamas; Cayman Islands; Cuba
Anguilla; Costa Rica; Guadeloupe; Puerto Rico; Turks and Caicos Islands; United States; Virgin Islands, British; Virgin Islands, U.S.
Upper elevation limit (metres): 1110
Range Map: Click here to open the map viewer and explore range.

Population [top]

Population: It is an extremely abundant species. It is spreading rapidly, with frequent new island records (Perry and Gerber, 2006).
Current Population Trend: Increasing
Additional data:
Population severely fragmented: No

Habitat and Ecology [top]

Habitat and Ecology: It generally inhabits mesic habitats but may be found in xeric habitat in the Bahamas, living in all kinds of disturbed habitats, including towns and houses. It is also present in forests, mangroves and coastal areas. It can also tolerate brackish water. It is found on the ground and on tree trunks. Males call from vegetation near pooled rainwater. Eggs are laid in still water, including pools, marshes, flood pastures, and ditches. It is competing with other species, and predates native amphibians in the wild. It might also be a vector for pathogens.

Breeding events have been found to last only one night and male mating behavior changes from acoustic competition to scramble searching over the breeding event. Most males have similar opportunities to mate with a female, and there doesn't appear to be a direct adaptive benefit for high mating selectivity by females, which can increase the invasive capacity of O. septentrionalis (Vargas Salinas, 2006).
Systems: Terrestrial; Freshwater

Use and Trade [top]

Use and Trade: It is common in the pet trade. Probably most of the trade is in captive-bred animals.

Threats [top]

Major Threat(s): There are no threats to this species. The species' diet suggests that it could severely impact native species, and its tadpoles impact those of some native anurans (see Perry and Gerber, 2006).

Conservation Actions [top]

Conservation Actions: It occurs in many protected areas.

Classifications [top]

1. Forest -> 1.5. Forest - Subtropical/Tropical Dry
suitability: Suitable  major importance:Yes
1. Forest -> 1.6. Forest - Subtropical/Tropical Moist Lowland
suitability: Suitable  major importance:Yes
1. Forest -> 1.7. Forest - Subtropical/Tropical Mangrove Vegetation Above High Tide Level
suitability: Suitable  major importance:Yes
1. Forest -> 1.8. Forest - Subtropical/Tropical Swamp
suitability: Suitable  major importance:Yes
1. Forest -> 1.9. Forest - Subtropical/Tropical Moist Montane
suitability: Suitable  major importance:Yes
3. Shrubland -> 3.6. Shrubland - Subtropical/Tropical Moist
suitability: Suitable  major importance:Yes
4. Grassland -> 4.6. Grassland - Subtropical/Tropical Seasonally Wet/Flooded
suitability: Suitable  major importance:Yes
5. Wetlands (inland) -> 5.1. Wetlands (inland) - Permanent Rivers/Streams/Creeks (includes waterfalls)
suitability: Marginal  
5. Wetlands (inland) -> 5.2. Wetlands (inland) - Seasonal/Intermittent/Irregular Rivers/Streams/Creeks
suitability: Marginal  
5. Wetlands (inland) -> 5.4. Wetlands (inland) - Bogs, Marshes, Swamps, Fens, Peatlands
suitability: Suitable  major importance:Yes
5. Wetlands (inland) -> 5.5. Wetlands (inland) - Permanent Freshwater Lakes (over 8ha)
suitability: Suitable  major importance:Yes
5. Wetlands (inland) -> 5.6. Wetlands (inland) - Seasonal/Intermittent Freshwater Lakes (over 8ha)
suitability: Suitable  major importance:Yes
5. Wetlands (inland) -> 5.7. Wetlands (inland) - Permanent Freshwater Marshes/Pools (under 8ha)
suitability: Suitable  major importance:Yes
5. Wetlands (inland) -> 5.8. Wetlands (inland) - Seasonal/Intermittent Freshwater Marshes/Pools (under 8ha)
suitability: Suitable  major importance:Yes
5. Wetlands (inland) -> 5.16. Wetlands (inland) - Permanent Saline, Brackish or Alkaline Marshes/Pools
suitability: Marginal  
13. Marine Coastal/Supratidal -> 13.4. Marine Coastal/Supratidal - Coastal Brackish/Saline Lagoons/Marine Lakes
suitability: Marginal  
14. Artificial/Terrestrial -> 14.1. Artificial/Terrestrial - Arable Land
suitability: Suitable  
14. Artificial/Terrestrial -> 14.2. Artificial/Terrestrial - Pastureland
suitability: Suitable  
14. Artificial/Terrestrial -> 14.3. Artificial/Terrestrial - Plantations
suitability: Suitable  
14. Artificial/Terrestrial -> 14.4. Artificial/Terrestrial - Rural Gardens
suitability: Suitable  
14. Artificial/Terrestrial -> 14.5. Artificial/Terrestrial - Urban Areas
suitability: Suitable  
14. Artificial/Terrestrial -> 14.6. Artificial/Terrestrial - Subtropical/Tropical Heavily Degraded Former Forest
suitability: Suitable  
15. Artificial/Aquatic & Marine -> 15.1. Artificial/Aquatic - Water Storage Areas (over 8ha)
suitability: Suitable  
15. Artificial/Aquatic & Marine -> 15.2. Artificial/Aquatic - Ponds (below 8ha)
suitability: Suitable  
15. Artificial/Aquatic & Marine -> 15.5. Artificial/Aquatic - Excavations (open)
suitability: Suitable  
15. Artificial/Aquatic & Marine -> 15.7. Artificial/Aquatic - Irrigated Land (includes irrigation channels)
suitability: Suitable  
15. Artificial/Aquatic & Marine -> 15.8. Artificial/Aquatic - Seasonally Flooded Agricultural Land
suitability: Suitable  
15. Artificial/Aquatic & Marine -> 15.9. Artificial/Aquatic - Canals and Drainage Channels, Ditches
suitability: Suitable  

In-Place Research, Monitoring and Planning
In-Place Land/Water Protection and Management
  Conservation sites identified:Yes, over entire range
  Occur in at least one PA:Yes
In-Place Species Management
In-Place Education
1. Research -> 1.2. Population size, distribution & trends
1. Research -> 1.3. Life history & ecology
3. Monitoring -> 3.1. Population trends

♦  Pets/display animals, horticulture
 International : ✓ 

♦  Establishing ex-situ production *

Bibliography [top]

Breuil, M. 2002. Histoire naturelle des Amphibiens et Reptiles terrestres de l'archipel Guadeloupéen. Guadeloupe, Saint-Martin, Saint-Barthélemy. Patrimoines Naturels 54: 1-339.

Breuil, M. 2004. Amphibiens et Reptiles des Antilles. PLB Editions, Guadeloupe.

Buurt, G. van. 2006. Conservation of amphibians and reptiles in Aruba, Curaçao and Bonaire. Applied Herpetology 3: 307-321.

Fong G., A. 2007. Monitoring amphibian populations in two sensitive habitats in Cuba.

Hedges, S.B. 1993. Global amphibian declines: a perspective from the Caribbean. Biodiversity and Conservation 2(3): 290-303.

Hedges, S.B. 1999. Distribution of amphibians in the West Indies. In: W.E. Duellman (ed.), Patterns of Distribution of Amphibians. A Global Perspective, pp. 211-254. The Johns Hopkins Press, Baltimore, Maryland.

Hedges, S.B. 2001. Caribherp: database of West Indian amphibians and reptiles ( Pennsylvania State University, University Park, PA.

Henderson, R.W. and Powell, R. 1999. West Indian herpetoecology. In: B.I. Crother (ed.), Caribbean Amphibians and Reptiles, pp. 223-226. Academic Press, San Diego, California.

Henderson, R.W. and Powell, R. 2001. Responses by the West Indian herpetofauna to human-influenced resources. Caribbean Journal of Science 37: 41-54.

IUCN. 2010. IUCN Red List of Threatened Species (ver. 2010.2). Available at: (Accessed: 29 June 2010).

Joglar, R.L. 1999. Que Cante el Coquí Ensayos, Cartas y Otros Documentos Sobre la Conservación de la Biodiversidad en Puerto Rico (1987-1999). Proyecto Coquí, Puerto Rico.

Joglar, R.L. and Rios, N. 1995. Osteopilus septentrionalis (Cuban Tree Frog, Rana Platanera) in Trujillo Alto, Puerto Rico. Herpetological Review: 105-106.

Joglar, R.L., Rios, N. and Cardona, M. 1998. Osteopilus septentrionalis (Cuban Tree Frog, Rana Platanera) in Coamo, Puerto Rico. Herpetological Review: 107.

Kaiser, H. and Henderson, R.W. 1994. The conservation status of Lesser Antillean frogs. Herpetological Natural History 2(2): 41-56.

Lorvelec, O., Pascal, M., Pavis, C. and Feldmann, P. 2007. Amphibians and reptiles of the French West Indies: Inventory, threats and conservation. Applied Herpetology 4: 131-161.

Meshaka Jr, W.E. 2001. The Cuban Treefrog in Florida: Life History of a Successful Colonizing Species. University Press of Florida, Gainesville, Florida.

Perry, G., and Gerber, G.P. 2006. Conservation of amphibians and reptiles in the British Virgin Islands: Status and patterns. Applied Herpetology: 237-256.

Powell, R. 2006. Conservation of the herpetofauna on the Dutch Windward Islands: St. Eustatius, Saba, and St. Maarten. Applied Herpetology 3: 293-306.

Powell, R., Passaro, R.J. and Henderson, R.W. 1992. Noteworthy herpetological records from Saint [sic] Maarten, Netherlands Antilles. Caribbean Journal of Science: 234-235.

Rivero, J.A. 1998. Los Anfibios y Reptiles de Puerto Rico / The Amphibians and Reptiles of Puerto Rico. Second edition. Editorial de la Universidad de Puerto Rico, San Juan.

Savage, J.M. 2002. The Amphibians and Reptiles of Costa Rica: A Herpetofauna between two Continents, between two Seas. University of Chicago Press, Chicago.

Schwartz, A. and Henderson, R.W. 1991. Amphibians and Reptiles of the West Indies: Descriptions, Distributions and Natural History. University of Florida Press, Gainesville, Florida.

Townsend, J.H., Eaton, J.M., Powell, R., Parmerlee, Jr, J.S. and Henderson, R.W. 2000. Cuban treefrogs (Osteopilus septentrionalis) in Anguilla, Lesser Antilles. Caribbean Journal of Science: 326-328.

Vargas Salinas, F. 2006. Breeding behavior and colonization success of the Cuban treefrog Osteopilus septentrionalis. Herpetologica 62(4): 398-408.

Citation: Blair Hedges, Luis Díaz, Beatrice Ibéné, Rafael Joglar, Robert Powell, Federico Bolaños, Gerardo Chaves. 2010. Osteopilus septentrionalis. The IUCN Red List of Threatened Species 2010: e.T55811A11368202. . Downloaded on 07 October 2015.
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